EP0453460A1 - Process for disposing of varnish or paint sludges and waste products of colouring agents. - Google Patents
Process for disposing of varnish or paint sludges and waste products of colouring agents.Info
- Publication number
- EP0453460A1 EP0453460A1 EP90901585A EP90901585A EP0453460A1 EP 0453460 A1 EP0453460 A1 EP 0453460A1 EP 90901585 A EP90901585 A EP 90901585A EP 90901585 A EP90901585 A EP 90901585A EP 0453460 A1 EP0453460 A1 EP 0453460A1
- Authority
- EP
- European Patent Office
- Prior art keywords
- waste
- coal dust
- mixture
- paint
- ground
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Granted
Links
- 239000002699 waste material Substances 0.000 title claims abstract description 33
- 238000000034 method Methods 0.000 title claims abstract description 23
- 239000003973 paint Substances 0.000 title claims description 14
- 239000004150 EU approved colour Substances 0.000 title 1
- 229940006093 opthalmologic coloring agent diagnostic Drugs 0.000 title 1
- 239000002966 varnish Substances 0.000 title 1
- ODINCKMPIJJUCX-UHFFFAOYSA-N Calcium oxide Chemical compound [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 claims abstract description 28
- 239000000292 calcium oxide Substances 0.000 claims abstract description 17
- 235000012255 calcium oxide Nutrition 0.000 claims abstract description 17
- 239000002904 solvent Substances 0.000 claims abstract description 13
- 239000000843 powder Substances 0.000 claims abstract description 9
- 235000019738 Limestone Nutrition 0.000 claims abstract description 8
- 238000001816 cooling Methods 0.000 claims abstract description 8
- 239000006028 limestone Substances 0.000 claims abstract description 8
- 239000002817 coal dust Substances 0.000 claims description 22
- 239000000203 mixture Substances 0.000 claims description 14
- 239000010802 sludge Substances 0.000 claims description 11
- 238000002485 combustion reaction Methods 0.000 claims description 8
- 239000000654 additive Substances 0.000 claims description 7
- BRPQOXSCLDDYGP-UHFFFAOYSA-N calcium oxide Chemical compound [O-2].[Ca+2] BRPQOXSCLDDYGP-UHFFFAOYSA-N 0.000 claims description 6
- 239000003086 colorant Substances 0.000 claims description 6
- 239000002734 clay mineral Substances 0.000 claims description 5
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims description 4
- 229910052799 carbon Inorganic materials 0.000 claims description 4
- 238000000926 separation method Methods 0.000 claims 1
- 239000003245 coal Substances 0.000 abstract description 4
- 239000003513 alkali Substances 0.000 abstract 1
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 8
- 229910001385 heavy metal Inorganic materials 0.000 description 6
- 239000007788 liquid Substances 0.000 description 4
- 229910052757 nitrogen Inorganic materials 0.000 description 4
- 239000002956 ash Substances 0.000 description 3
- 238000000227 grinding Methods 0.000 description 3
- 239000004922 lacquer Substances 0.000 description 3
- 239000004484 Briquette Substances 0.000 description 2
- 239000004566 building material Substances 0.000 description 2
- 239000007789 gas Substances 0.000 description 2
- 238000011084 recovery Methods 0.000 description 2
- 150000003464 sulfur compounds Chemical class 0.000 description 2
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 2
- 235000002918 Fraxinus excelsior Nutrition 0.000 description 1
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 description 1
- 230000000996 additive effect Effects 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 239000011248 coating agent Substances 0.000 description 1
- 238000000576 coating method Methods 0.000 description 1
- 239000000428 dust Substances 0.000 description 1
- 239000000975 dye Substances 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 239000008187 granular material Substances 0.000 description 1
- 239000003673 groundwater Substances 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 238000012432 intermediate storage Methods 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 238000002844 melting Methods 0.000 description 1
- 230000008018 melting Effects 0.000 description 1
- 238000002156 mixing Methods 0.000 description 1
- 239000000049 pigment Substances 0.000 description 1
- 229920005596 polymer binder Polymers 0.000 description 1
- 239000002491 polymer binding agent Substances 0.000 description 1
- 238000002360 preparation method Methods 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 229910052717 sulfur Inorganic materials 0.000 description 1
- 239000011593 sulfur Substances 0.000 description 1
Classifications
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G5/00—Incineration of waste; Incinerator constructions; Details, accessories or control therefor
- F23G5/02—Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/30—Fuel from waste, e.g. synthetic alcohol or diesel
Definitions
- the present invention relates to a process for the disposal of paint and color sludge and colorant waste, in particular from the automotive industry, but also from other branches of industry in which larger quantities of this problematic waste are produced and have hitherto only been able to be disposed of in special landfills to be spent.
- the space in special landfills is limited and costly, so that there is an urgent need to avoid waste that could previously only be disposed of in special landfills or to dispose of it in an environmentally friendly manner with material / energy recovery.
- Lacquer and color sludge but also colorant waste generally contain more or less large amounts of vaporizable solvents, more or less high polymer binders, inorganic and / or organic dyes and / or pigments. In many cases, they also contain not insignificant amounts of heavy metals, so that they can endanger the groundwater if not properly landfilled. Attempts to burn these problematic waste materials have so far failed because these waste materials are mostly viscous and sticky and cannot even be dissolved or suspended with the addition of other solvents to such an extent that they can be metered into the incineration plants without problems.
- the object of the invention is to develop a process for the disposal of paint and color sludge and colorant waste, in particular from the automotive industry, which is generally applicable and leads to waste materials which can be disposed of easily and inexpensively.
- This task can be solved surprisingly simply by grinding the waste and burning it together with at least the same amount of coal dust.
- the wastes are only ground after the vaporizable solvents have been largely removed.
- Evaporable solvents are generally only separated off if this is possible, for example by gentle heating and suction, if appropriate under reduced pressure, and the solvent vapors obtained can be easily recovered or burned without problems.
- a preparation or recovery system for solvent vapors already exists, it can be useful and economical to separate evaporable solvents to a greater or lesser extent and thus to process them separately.
- vaporizable solvents can also remain in the waste and be disposed of together with the other components of the paint and color sludge and colorant waste.
- these ground waste materials are mixed and burned in a special embodiment with at least the same amount by weight of coal dust and optionally alkaline additives, preferably quicklime and / or limestone powder.
- coal dust grades usually obtained in power plants can be used as coal dust. If desired, however, more intensive and finer grinding can also take place. The finer the coal dust, the greater the amount of evaporable solvent that can be bound by it.
- Alkaline additives preferably quicklime and / or limestone powder
- the amount of alkaline additives, preferably quicklime and / or limestone powder should be more than stoichiometric, based on the content of heavy metals and / or sulfur compounds, in order to ensure that these components are sufficiently incorporated in the ash and to escape Prevent components with the exhaust gases into the atmosphere.
- the addition of quicklime is also recommended if the waste contains a considerable amount of water as a vaporizable solvent, since this can react with the quicklime when mixed and therefore no longer has to be bound by finely divided carbon.
- the mixture of ground waste and coal dust and optionally alkaline additives preferably quicklime and / or limestone powder
- These briquettes can be stored without any problems and can be burned directly in appropriate incineration plants if required. If it is intended to carry out the combustion in pulverized coal incineration plants, these briquettes can optionally be milled again. The resulting briquette dust can then be burned without any problems either on its own or in a mixture with further coal dust.
- up to 50% by weight of the coal dust can be replaced in the mixture of ground waste and coal dust and optionally quicklime and / or limestone powder by finely divided substances from combustion plants which have an increased content of unburned carbon and / or free calcium oxide and / or unsintered clay minerals.
- Such finely divided residues from incineration plants are themselves problematic and costly to dispose of. For example, ashes with an increased amount of unburned coal dust are unsuitable for use in the building materials industry. In the method according to the invention, this unburned carbon is fed back to an incineration plant and is even used to generate energy. Further problematic residues from incineration plants can be those which have a considerable proportion of free calcium oxide.
- residues from dry additive processes there are qualities that are difficult or impossible to use in the building materials industry.
- qualities that are difficult or impossible to use in the building materials industry are excellently suitable for use in the process according to the invention, in particular when it is necessary to add quicklime and / or limestone powder in order to be able to burn waste containing heavy metals and / or sulfur according to the invention.
- residues from incineration plants with an increased content of unsintered clay minerals can also be used.
- residues include, in particular, fluidized bed ash from coal with a high content of clay minerals. Such fluidized-bed pockets have hitherto not been usable or can only be used with difficulty.
- the process according to the invention are capable of absorbing at least some of the liquid components of the waste when mixed and thereby facilitating the intermediate storage and, if appropriate, briquetting.
- temperatures are so high that the absorbed components are released again and the proportions of clay minerals are sintered or melted.
- the release of heavy metals during the combustion process is largely prevented by using the above-mentioned residues or other alkaline additives.
- the heavy metals contained in the paint and paint sludge or paint waste are immobilized by glazing in the granulate.
- the content of such problematic residues from incineration plants can be up to 50% by weight of the coal dust. If the content is higher, there is a risk that the mixtures according to the invention will no longer release enough energy during the combustion in order to ensure sufficiently high combustion temperatures. Although in many cases the addition of the same weight of coal dust to the waste is sufficient, it is advantageous for the reasons mentioned above that the mixture contains two to ten times the amount of coal dust based on the waste content. In particular with a higher content of coal dust in the mixture to be burned, problematic residues from incineration plants can also be used and disposed of according to the invention.
- Lacquer sludge from an automobile factory was ground with liquid nitrogen under cooling and mixed with three times the amount of coal dust from the power plant and briquetted. Briquettes were easy to grind and could easily be burned.
- Lacquer sludge from the metallic coating of an automobile factory was finely ground while cooling with liquid nitrogen and mixed with three times the amount of coal dust from the power plant mill and briquetted.
- the briquettes were easy to grind and could be burned without problems.
- 10% quicklime was added to the mixture. This mixture was also easy to briquette, grindable and combustible.
Landscapes
- Engineering & Computer Science (AREA)
- Mechanical Engineering (AREA)
- General Engineering & Computer Science (AREA)
- Processing Of Solid Wastes (AREA)
- Solid Fuels And Fuel-Associated Substances (AREA)
- Treatment Of Sludge (AREA)
- Manufacture Of Porous Articles, And Recovery And Treatment Of Waste Products (AREA)
- Paints Or Removers (AREA)
Abstract
Ce procédé est destiné en particulier à l'industrie automobile. On broye les déchets, en séparant le cas échéant une grande partie des solvants évaporables, le cas échéant en les refroidissant, puis on les mélange avec une quantité en poids au moins égale de poudre de charbon et, le cas échéant, avec des produits d'addition alcalins, de préférence de la chaux vive et/ou de la poudre de pierre à chaux; finalement, on brûle le produit ainsi obtenu.This process is intended in particular for the automotive industry. The waste is crushed, separating, if necessary, a large part of the evaporable solvents, if necessary by cooling them, then they are mixed with an at least equal quantity by weight of coal powder and, where appropriate, with products of alkali addition, preferably quicklime and / or limestone powder; finally, the product thus obtained is burnt.
Description
Claims
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
AT90901585T ATE85356T1 (en) | 1989-01-10 | 1990-01-05 | DISPOSAL PROCEDURES FOR PAINT AND PAINT SLUDGE AND PAINT WASTE. |
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
DE3900482A DE3900482C1 (en) | 1989-01-10 | 1989-01-10 | |
DE3900482 | 1989-01-10 |
Publications (2)
Publication Number | Publication Date |
---|---|
EP0453460A1 true EP0453460A1 (en) | 1991-10-30 |
EP0453460B1 EP0453460B1 (en) | 1993-02-03 |
Family
ID=6371793
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
EP90901585A Expired - Lifetime EP0453460B1 (en) | 1989-01-10 | 1990-01-05 | Process for disposing of varnish or paint sludges and waste products of colouring agents |
Country Status (7)
Country | Link |
---|---|
EP (1) | EP0453460B1 (en) |
JP (1) | JPH04505627A (en) |
BR (1) | BR9007012A (en) |
DD (1) | DD291617A5 (en) |
DE (2) | DE3900482C1 (en) |
ES (1) | ES2038053T3 (en) |
WO (1) | WO1990008178A1 (en) |
Families Citing this family (8)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
DE3924312C2 (en) * | 1989-07-22 | 1994-06-09 | Gfr Aufbereitung Reststoffe | Process and device for recycling residues, paint and paint sludges |
NL9002193A (en) * | 1990-10-09 | 1992-05-06 | Leto Recycling Bv | METHOD AND APPARATUS FOR PROCESSING WASTE. |
DE4331674C1 (en) * | 1993-09-17 | 1995-01-26 | Herberts Gmbh | Process for the preparation of aqueous coating compositions involving the recycling of paint sludge; the coating compositions obtained in this process, and the use thereof |
DE4340513C2 (en) * | 1993-11-27 | 2000-09-21 | Ver Verwertung Und Entsorgung | Process for the preparation of residues for subsequent recycling and device for carrying out the process |
DE19512550C1 (en) * | 1995-04-06 | 1996-06-20 | Lindemann Maschfab Gmbh | Method and device for processing containers |
DE60028250D1 (en) * | 1999-12-30 | 2006-06-29 | Gert Hjort Jensen | PROCESS FOR USE OF POWDER MATERIALS |
US8057556B2 (en) * | 2007-01-23 | 2011-11-15 | Citibank, N.A. | Processing paint sludge to produce a combustible fuel product |
JP5456341B2 (en) * | 2009-03-17 | 2014-03-26 | 太平洋セメント株式会社 | Method for producing waste oil-based solid fuel and method for using the waste oil-based solid fuel |
Family Cites Families (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
DE1471600A1 (en) * | 1963-07-23 | 1969-04-10 | Oel Werk Tedden Gmbh | Process for converting the acidic, resinous residues resulting from the refining of hydrocarbons with sulfuric acid into flammable substances |
DE2451038C2 (en) * | 1974-10-26 | 1982-11-18 | Vereinigte Flugtechnische Werke Gmbh, 2800 Bremen | Process for the environmentally friendly disposal of organic waste and / or residues of animal origin |
DE2935103C2 (en) * | 1979-08-30 | 1987-03-26 | Estermann, Thomas M., Gempen, Basel | Use of liquid or viscous industrial waste as an additional fuel in industrial combustion processes |
-
1989
- 1989-01-10 DE DE3900482A patent/DE3900482C1/de not_active Expired - Fee Related
-
1990
- 1990-01-05 DE DE9090901585T patent/DE59000852D1/en not_active Expired - Fee Related
- 1990-01-05 WO PCT/EP1990/000020 patent/WO1990008178A1/en active IP Right Grant
- 1990-01-05 ES ES199090901585T patent/ES2038053T3/en not_active Expired - Lifetime
- 1990-01-05 EP EP90901585A patent/EP0453460B1/en not_active Expired - Lifetime
- 1990-01-05 JP JP2502169A patent/JPH04505627A/en active Pending
- 1990-01-05 BR BR909007012A patent/BR9007012A/en not_active Application Discontinuation
- 1990-01-08 DD DD90336989A patent/DD291617A5/en not_active IP Right Cessation
Non-Patent Citations (1)
Title |
---|
See references of WO9008178A1 * |
Also Published As
Publication number | Publication date |
---|---|
DD291617A5 (en) | 1991-07-04 |
ES2038053T3 (en) | 1993-07-01 |
DE3900482C1 (en) | 1990-02-22 |
EP0453460B1 (en) | 1993-02-03 |
JPH04505627A (en) | 1992-10-01 |
DE59000852D1 (en) | 1993-03-18 |
BR9007012A (en) | 1991-11-12 |
WO1990008178A1 (en) | 1990-07-26 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
DE69623034T2 (en) | WASTE TREATMENT METHOD AND DEVICE | |
DE69027675T2 (en) | DEVICE AND METHOD FOR TREATING WASTE | |
EP0110208B1 (en) | Process for the utilisation of sludge | |
DE2624971C2 (en) | Process for the recovery of industrial waste | |
EP0293982B1 (en) | Process for the treatment of contaminated mineral materials | |
EP0453460B1 (en) | Process for disposing of varnish or paint sludges and waste products of colouring agents | |
DD237479A5 (en) | METHOD FOR PRODUCING AN ABSORPTION AND ADSORPTION AGENT, AND ABSORPTION AND ADSORPTION AGENT PRODUCED ACCORDING TO THIS PROCESS | |
EP0543133A1 (en) | Process and installation for treating thickened sewage sludge | |
WO1988001989A1 (en) | Process for manufacturing a calcium sulphate-containing solid secondary raw material | |
DE3924312A1 (en) | METHOD AND DEVICE FOR RECYCLING RESIDUES FROM LACQUERIES ETC. | |
DE3632364C2 (en) | Process for the extraction of secondary raw materials | |
EP0383229B1 (en) | Preparation of iron-containing sludge for further processing | |
DE4111442C1 (en) | ||
DE19513832B4 (en) | Process for recycling residual and waste materials by combining a fluidized-bed thermolysis with an entrainment gasification | |
WO1992022511A1 (en) | Process for preparing and possibly solidifying filter dusts and/or reaction products | |
WO1989001505A1 (en) | Process and installation for recovering reusable gas from waste through pyrolysis | |
EP1892281A1 (en) | Process for making a substitute fuel for use in coal fired power plants and/or waste incineration plants and/or cement manufacturing plants or other incinerators that use solid fuels | |
DE102007004145A1 (en) | Production of shaped products for combustion in pellet combustion plants comprises mixing of chopped wood with a fluidity improving agent e.g. sewage sludge and producing shaped products in the form of pellets using a screw-type extruder | |
DE4243337C1 (en) | Explosive material disposal - uses water with deactivated material to give a soln. of potassium nitrate for further use | |
DE2264924A1 (en) | Fixed bed gasification system - using crushed coal and tar extruded and briquetted directly into producer shaft | |
DE3227000A1 (en) | Process for the production of a storage-stable product, in particular a product capable of being disposed of in landfill, from filter sludges, sinter sludges or oil separator sludges having iron oxide residues and oil residues contained in the dry matter | |
EP0873383B1 (en) | Process for producing granulated, pourable fuel | |
DE4320441C2 (en) | Process for the production of thermostable moldings from mixed contaminated plastic waste | |
DE4123368C1 (en) | ||
DE2942638C2 (en) | Use of a powder consisting of highly viscous oils or the like and hydrated calcium oxide as fuel for dust-fired systems |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
PUAI | Public reference made under article 153(3) epc to a published international application that has entered the european phase |
Free format text: ORIGINAL CODE: 0009012 |
|
17P | Request for examination filed |
Effective date: 19910706 |
|
AK | Designated contracting states |
Kind code of ref document: A1 Designated state(s): AT BE DE ES FR GB IT NL SE |
|
17Q | First examination report despatched |
Effective date: 19920325 |
|
GRAA | (expected) grant |
Free format text: ORIGINAL CODE: 0009210 |
|
AK | Designated contracting states |
Kind code of ref document: B1 Designated state(s): AT BE DE ES FR GB IT NL SE |
|
REF | Corresponds to: |
Ref document number: 85356 Country of ref document: AT Date of ref document: 19930215 Kind code of ref document: T |
|
ITF | It: translation for a ep patent filed | ||
REF | Corresponds to: |
Ref document number: 59000852 Country of ref document: DE Date of ref document: 19930318 |
|
ET | Fr: translation filed | ||
GBT | Gb: translation of ep patent filed (gb section 77(6)(a)/1977) |
Effective date: 19930416 |
|
REG | Reference to a national code |
Ref country code: ES Ref legal event code: FG2A Ref document number: 2038053 Country of ref document: ES Kind code of ref document: T3 |
|
PLBE | No opposition filed within time limit |
Free format text: ORIGINAL CODE: 0009261 |
|
STAA | Information on the status of an ep patent application or granted ep patent |
Free format text: STATUS: NO OPPOSITION FILED WITHIN TIME LIMIT |
|
26N | No opposition filed | ||
EAL | Se: european patent in force in sweden |
Ref document number: 90901585.1 |
|
PGFP | Annual fee paid to national office [announced via postgrant information from national office to epo] |
Ref country code: GB Payment date: 19961216 Year of fee payment: 8 Ref country code: FR Payment date: 19961216 Year of fee payment: 8 |
|
PGFP | Annual fee paid to national office [announced via postgrant information from national office to epo] |
Ref country code: SE Payment date: 19970123 Year of fee payment: 8 Ref country code: BE Payment date: 19970123 Year of fee payment: 8 |
|
PGFP | Annual fee paid to national office [announced via postgrant information from national office to epo] |
Ref country code: AT Payment date: 19970124 Year of fee payment: 8 |
|
PGFP | Annual fee paid to national office [announced via postgrant information from national office to epo] |
Ref country code: NL Payment date: 19970131 Year of fee payment: 8 Ref country code: ES Payment date: 19970131 Year of fee payment: 8 |
|
PGFP | Annual fee paid to national office [announced via postgrant information from national office to epo] |
Ref country code: DE Payment date: 19971222 Year of fee payment: 9 |
|
PG25 | Lapsed in a contracting state [announced via postgrant information from national office to epo] |
Ref country code: GB Free format text: LAPSE BECAUSE OF NON-PAYMENT OF DUE FEES Effective date: 19980105 Ref country code: AT Free format text: LAPSE BECAUSE OF NON-PAYMENT OF DUE FEES Effective date: 19980105 |
|
PG25 | Lapsed in a contracting state [announced via postgrant information from national office to epo] |
Ref country code: SE Free format text: LAPSE BECAUSE OF NON-PAYMENT OF DUE FEES Effective date: 19980106 |
|
PG25 | Lapsed in a contracting state [announced via postgrant information from national office to epo] |
Ref country code: ES Free format text: LAPSE BECAUSE OF EXPIRATION OF PROTECTION Effective date: 19980107 |
|
PG25 | Lapsed in a contracting state [announced via postgrant information from national office to epo] |
Ref country code: FR Free format text: THE PATENT HAS BEEN ANNULLED BY A DECISION OF A NATIONAL AUTHORITY Effective date: 19980131 Ref country code: BE Free format text: LAPSE BECAUSE OF NON-PAYMENT OF DUE FEES Effective date: 19980131 |
|
BERE | Be: lapsed |
Owner name: VW KRAFTWERK G.M.B.H. Effective date: 19980131 Owner name: G.- FUR DIE AUFBEREITUNG UND VERWERTUNG VON RESTST Effective date: 19980131 |
|
PG25 | Lapsed in a contracting state [announced via postgrant information from national office to epo] |
Ref country code: NL Free format text: LAPSE BECAUSE OF NON-PAYMENT OF DUE FEES Effective date: 19980801 |
|
GBPC | Gb: european patent ceased through non-payment of renewal fee |
Effective date: 19980105 |
|
NLV4 | Nl: lapsed or anulled due to non-payment of the annual fee |
Effective date: 19980801 |
|
EUG | Se: european patent has lapsed |
Ref document number: 90901585.1 |
|
REG | Reference to a national code |
Ref country code: FR Ref legal event code: ST |
|
PG25 | Lapsed in a contracting state [announced via postgrant information from national office to epo] |
Ref country code: DE Free format text: LAPSE BECAUSE OF NON-PAYMENT OF DUE FEES Effective date: 19991103 |
|
REG | Reference to a national code |
Ref country code: ES Ref legal event code: FD2A Effective date: 20000301 |
|
PG25 | Lapsed in a contracting state [announced via postgrant information from national office to epo] |
Ref country code: IT Free format text: LAPSE BECAUSE OF NON-PAYMENT OF DUE FEES;WARNING: LAPSES OF ITALIAN PATENTS WITH EFFECTIVE DATE BEFORE 2007 MAY HAVE OCCURRED AT ANY TIME BEFORE 2007. THE CORRECT EFFECTIVE DATE MAY BE DIFFERENT FROM THE ONE RECORDED. Effective date: 20050105 |